Kligerman A D, Hu Y
B143-06, Cellular Toxicology Branch, Environmental Carcinogenesis Division, National Health and Environmental Effects Research Laboratory, U.S. Environmental Protection Agency, Research Triangle Park, NC 27711, USA.
Chem Biol Interact. 2007 Mar 20;166(1-3):132-9. doi: 10.1016/j.cbi.2006.03.013. Epub 2006 Apr 18.
1,3-Butadiene (BTD) is an important commodity chemical and air pollutant that has been shown to be a potent carcinogen in mice, and to a lesser extent, a carcinogen in rats. To better assess butadiene's carcinogenic risk to humans, it is important to understand its mode of action and how this relates to differences in responses among species. In a series of in vitro experiments, lymphocytes from rats, mice, and humans were exposed to 3,4-epoxy-1-butene (EB) or 1,2:3,4-diepoxybutane (DEB) for 1h at the G(0) stage of the cell cycle, stimulated to divide, and cultured to assess the ability of these metabolites to induce sister chromatid exchange (SCE) and chromosome aberrations (CAs). EB induced no increases in SCEs or CAs in the cells from the three species. DEB was a potent SCE- and CA-inducer, with the results being similar in each rodent species. The response for SCEs seen in the human cells was more complex, with genetic polymorphism for glutathione-S-transferases (GST) possibly modulating the response. The single cell gel electrophoresis assay was used on genetically engineered V79 cell lines to investigate a possible influence of GST status. Experiments were also conducted to investigate the reason for EB's failure to induce SCEs or CAs in G(0) cells. The results indicate that EB-induced DNA damage was repaired before DNA synthesis in unstimulated lymphocytes, but EB caused a large increase in SCEs if actively cycling cells were treated. Thus, the results indicate that DEB damage is persistent in G(0) cells, and DEB is a much more potent genotoxicant than EB. The carcinogenic effect of butadiene will most likely depend on the degree to which DEB is produced and reaches target tissues, and to a lesser extent on the ability of EB to reach actively dividing or repair deficient cells.
1,3 - 丁二烯(BTD)是一种重要的化工商品和空气污染物,已被证明是小鼠的强效致癌物,在大鼠中致癌性稍弱。为了更好地评估丁二烯对人类的致癌风险,了解其作用模式以及这与物种间反应差异的关系非常重要。在一系列体外实验中,将来自大鼠、小鼠和人类的淋巴细胞在细胞周期的G(0)期暴露于3,4 - 环氧 - 1 - 丁烯(EB)或1,2:3,4 - 二环氧丁烷(DEB)1小时,刺激其分裂并培养,以评估这些代谢物诱导姐妹染色单体交换(SCE)和染色体畸变(CA)的能力。EB未导致三种物种细胞中SCE或CA增加。DEB是强效的SCE和CA诱导剂,在每种啮齿动物物种中的结果相似。人类细胞中观察到的SCE反应更为复杂,谷胱甘肽 - S - 转移酶(GST)的基因多态性可能调节该反应。对基因工程V79细胞系进行单细胞凝胶电泳分析,以研究GST状态的可能影响。还进行了实验以探究EB在G(0)细胞中未能诱导SCE或CA的原因。结果表明,EB诱导的DNA损伤在未刺激的淋巴细胞中DNA合成之前就已修复,但如果处理活跃分裂的细胞,EB会导致SCE大幅增加。因此,结果表明DEB损伤在G(0)细胞中持续存在,并且DEB比EB是更强效的遗传毒性剂。丁二烯的致癌作用很可能取决于DEB产生并到达靶组织的程度,在较小程度上取决于EB到达活跃分裂或修复缺陷细胞的能力。